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EC Regulation 854/2004 CLASSIFICATION of BIVALVE MOLLUSC PRODUCTION AREAS in ENGLAND and WALES SANITARY SURVEY REPORT

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EC Regulation 854/2004 CLASSIFICATION of BIVALVE MOLLUSC PRODUCTION AREAS in ENGLAND and WALES SANITARY SURVEY REPORT EC Regulation 854/2004 CLASSIFICATION OF BIVALVE MOLLUSC PRODUCTION AREAS IN ENGLAND AND WALES SANITARY SURVEY REPORT Fowey Estuary (Cornwall) 2010 SANITARY SURVEY REPORT FOWEY ESTUARY Cover photo: oyster trestles at Pont Pill - Relay. CONTACTS: For enquires relating to this report or For enquires relating to policy matters further information on the on the implementation of Sanitary implementation of Sanitary Surveys in Surveys in England and Wales: England and Wales: Food Safety Group Linden Jack Cefas Weymouth Laboratory Hygiene and Microbiology Division Barrack Road (Policy Unit) The Nothe Food Standards Agency Weymouth Third Floor Zone C Aviation House Dorset 125 Kingsway DT43 8UB London WC2B 6NH ( +44 (0) 1305 206600 ( +44 (0) 20 7276 8955 * [email protected] * [email protected] © Crown copyright, 2010. Overall Review of Production Area 2 SANITARY SURVEY REPORT FOWEY ESTUARY STATEMENT OF USE: This report provides information from a desk study evaluation of the information available relevant to perform a sanitary survey of bivalve mollusc production areas in the Fowey Estuary, Cornwall. Its primary purpose is to demonstrate compliance with the requirements for classification of bivalve mollusc production areas in EC Regulation 854/2004, laying down specific rules for the organisation of official controls on products of animal origin intended for human consumption. The Centre for Environment, Fisheries and Aquaculture Science (Cefas) undertook this work on behalf of the Food Standards Agency (FSA). DISSEMINATION: Food Standards Agency, Fowey Port Health Authority, Environment Agency. Overall Review of Production Area 3 SANITARY SURVEY REPORT FOWEY ESTUARY CONTENTS 1. INTRODUCTION 2. SHELLFISHERIES 3. OVERALL ASSESSMENT 4. RECOMMENDATIONS 5. SAMPLING PLAN APPENDICES I. Human population II. Hydrometric data: rainfall III. Hydrometric data: freshwater inputs IV. Hydrodynamic data: bathymetry V. Hydrodynamic data: tides and currents VI. Meteorological data: wind VII. Sources and variation of microbiological pollution: sewage discharges VIII. Sources and variation of microbiological pollution: agriculture IX. Sources and variation of microbiological pollution: birds X. Sources and variation of microbiological pollution: boats XI. Microbiological data: water XII. Microbiological data: shellfish flesh XIII. Shoreline survey References List of Abbreviations Glossary Acknowledgements Overall Review of Production Area 4 SANITARY SURVEY REPORT FOWEY ESTUARY 1 INTRODUCTION 1.1 LEGISLATIVE REQUIREMENT Filter feeding, bivalve molluscan shellfish (e.g. oysters, mussels) retain and accumulate a variety of microorganisms from their natural environments. Since filter feeding promotes retention and accumulation of microorganisms, the microbiological safety of bivalve molluscs for human consumption depends heavily on the quality of the waters from which they are taken (Bell, 2006). When consumed raw or lightly cooked, bivalves contaminated with pathogenic microorganisms may cause infectious diseases (e.g. Norovirus-associated gastroenteritis, Hepatitis A and Salmonellosis) in humans. Infectious disease outbreaks are more likely to occur in coastal areas where bivalve mollusc production areas (BMPAs) are impacted by sources of human and or animal microbiological contamination. In England and Wales, fish and shellfish constitute the fourth most reported food item causing infectious disease outbreaks in humans after poultry, red meat and desserts (Hughes et al., 2007). The risk of contamination of shellfish with pathogens is assessed through the microbiological monitoring of shellfish. This assessment results in the classification of BMPAs, which determines the level of treatment (e.g. purification, relaying, cooking) required before human consumption of bivalves (Lee and Younger, 2002). Under EC Regulation 854/20041, laying down specific rules for the organisation of official controls on products of animal origin intended for human consumption, competent authorities are required to undertake a number of activities collectively known (in England and Wales) as “sanitary surveys”. The Centre for Environment Fisheries and Aquaculture Science (Cefas) is performing sanitary surveys for new BMPAs in England and Wales, on behalf of the Food Standards Agency (FSA). The purpose of these sanitary surveys is to demonstrate compliance with the requirements stated in Annex II (Chapter II, paragraph 6) of EC Regulation 854/2004, whereby if the competent authority decides in principle to classify a production or relay area it must: a) make an inventory the sources of pollution of human or animal origin likely to be a source of contamination for the production area; b) examine the quantities of organic pollutants which are released during the different periods of the year, according to the seasonal variations of both human and animal populations in the catchment area, rainfall readings, waste-water treatment, etc.; c) determine the characteristics of the circulation of pollutants by virtue of 1 See Section 6, Annex II of the Regulation. Overall Review of Production Area 5 SANITARY SURVEY REPORT FOWEY ESTUARY current patterns, bathymetry and the tidal cycle in the production area; and d) establish a sampling programme of bivalve molluscs in the production area which is based on the examination of established data, and with a number of samples, a geographical distribution of the sampling points and a sampling frequency which must ensure that the results of the analysis are as representative as possible for the area considered.” EC Regulation 854/2004 also specifies the use of Escherichia coli as an indicator of microbiological contamination in bivalves. This bacterium is present in animal and human faeces and is therefore indicative of contamination of faecal origin. In addition to better targeting the location of RMPs and frequency of monitoring, it is believed that sanitary surveys may serve to help to target future water quality improvements and better analyse their effects on BMPAs. Improved monitoring should lead to improved detection of pollution events and identification of the likely sources of pollution. Remedial action may then be possible either through funding of improvements in point sources of contamination or as a result of changes in land management practices. This report documents the quantitative assessment made of the levels of microbiological contamination in bivalves from the Fowey Estuary, Cornwall and presents the recommended sampling plan as a result of a sanitary survey undertaken by Cefas on behalf of the Food Standards Agency (FSA). Overall Review of Production Area 6 SANITARY SURVEY REPORT FOWEY ESTUARY 1.2 SITE DESCRIPTION FOWEY ESTUARY The Fowey Estuary is situated in south Cornwall, southwest coast of England (Figure 1.1). It is a flooded river valley ria (drowned river valley) formed by post glacial sea level rise infiltrating river valleys during the last ice age. The estuary is approximately 11km in length covering approximately 4km2 at high tide. Table 1.1 summarises the main morphological characteristics of the estuary. The outline is branching and the entrance to the estuary is relatively narrow with bedrock shores leading to sedimentary shorelines further into the estuary between Mixtow (Figure 1.2) and Golant and in small tributaries such as Pont Pill creek (Figure 1.3). Table 1.1 Main characteristics of the Fowey Estuary. Geomorphological type Ria Shoreline length (km) 39.2 Core area (ha) 304.8 Intertidal area (ha) 146 Data from the Estuary Guide (ABPmer and Wallingford, 2009). Intertidal refers to the area between MHWS and MLWN tidal levels. Figure 1.1 Aerial view of the Fowey Estuary showing its main localities and tributaries. Reproduced under licence Google Earth™ mapping service. Overall Review of Production Area 7 SANITARY SURVEY REPORT FOWEY ESTUARY Figure 1.2 Aerial view of the Fowey Estuary at Mixtow. Reproduced under licence Google Earth™ mapping service. Overall Review of Production Area 8 SANITARY SURVEY REPORT FOWEY ESTUARY Figure 1.3 Aerial view of the Fowey Estuary at Pont Pill. Reproduced under licence Google Earth™ mapping service. From Golant, there is a shallow gradient through open moorland with low intensity “hill” farming leading into steep sided wooded valley where it continues to flow through wooden valleys bounded by agricultural land use. The upper reaches of the estuary have largely silted up leaving extensive mudflats (Figure 1.4) and sandflats. Overall Review of Production Area 9 SANITARY SURVEY REPORT FOWEY ESTUARY Figure 1.4 Middle reaches of Pont Pill at low tide. Photo courtesy of Philip Halling. The Fowey Estuary is biologically rich, both in terms of biodiversity and habitats. These are recognised by a number of nature conservation designations: Lantic Bay is a Special Area of Conservation (SAC), and there are various Special Sites of Scientific Interest (SSSI). The upper reaches of the River Fowey flow through an Area of Outstanding Natural Beauty (AONB) and a Special Area of Great Landscape Value. The estuary itself is also within the boundary of an AONB. The main commercial uses of the estuary include shipping, coastal fisheries and tourism, in particular water-based activities (e.g. rowing, canoeing, sub- aqua). Fowey is also a busy commercial China Clay port (Figure 1.5). The estuary contains several designated areas for salmon, sea trout, eels and bass fisheries. Bait harvesting also takes place in estuary. Overall Review of Production Area 10 SANITARY
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